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Houk, Vernon N.

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Roport/Artldo TitlB RePort of Science Panel to the Agent Orange Working
Group with Science Panel Review of Proposed Protocol
Design for Veterans Administration Epidemiology
Study, dated March 5, 1982

Journal/Book Title
Year

1982

Month/Day
Color
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D

6

Doscripton Notes

Tuesday, March 19, 2002

Page 5588 of 5611

�REPORT OF SCIENCE PANEL
TO THE

AGENT ORANGE WORKING GROUP

There have been several meetings of the Science Panel since my last report.
Protocol Review
The Science Panel completed its review of the National Cancer Institute
(NCI) "A Case-Control Study of Lymphoma and Soft-Tissue Sarcoma:
Association with Herbicide Exposures." It was agreed that the individual
reviews will be returned to NCI. In general, the Science Panel was
supportive of the proposal, and several agencies offered to help provide
specific information. We further noted that this study should be complementary to the NIOSH proposed case control study on soft tissue sarcoma.
The two studies are not exclusive of one another.
Status of Fat Biopsies
The Chairman of the Fat Biopsy Subcommittee reported that the Subcommittee
is developing a report to the Science Panel on fat biopsies for dioxins
that will include information on (a) what is currently known and the current
status, (b) when we would recommend it be done and under what circumstances,
and (c) its limitations. It is anticipated that this report will be available
in the near future.
Assessment of Agent Orange Health Hazards in the Population in Vietnam
Recent press reports of a group returning from Vietnam indicated that the
Government of Vietnam would welcome assessment of the health risks in the
Vietnam population by American scientists. There is concern about the
status of the records and the availability of those records in Vietnam.
Dr. T. E. Woodward, VA distinguished physician, reported that he found the
records to be useful. There was general agreement that a study would be
difficult to do and difficult to interpret. We believe that assessing
exposure would be virtually impossible.
Public Information
A member of the Science Panel expressed concern that the public does not
have information available to counter some of the claims of adverse health
effects which are not yet proven. There was general discussion of this
topic. Most members feel that there is insufficient data to make firm
statements on these issues at the moment.
The Veterans Administration Mortality Study
The Subcommittee reviewing the proposed Veterans Administration Mortality
Study has reached consensus on recommendations to be made to the Veterans
Administration. These will be forthcoming to the Chair, Agent Orange
Working Group within the next 2 weeks.

�Review of the Veterans Administration Epidemiology Study
The Science Panel concluded its review of the Veterans Administration
Epidemiology Study proposed protocol from the University of California at
Los Angeles. A detailed review has been submitted to the Chair, Agent
Orange Working Group for transmittal to the Veterans Administration. In
summary, on the basis of the present document, the panel believes it is
possible to begin the pilot phase of the study. The selection of the
cohort for the Pilot Study should immediately proceed as well as the quality
control and quality assurance procedures, the redesign of the questionnaire,
and the determination of comparability and interpretation of some of the
proposed instruments, such as nerve conduction studies, spirometry, etc.,
between examining centers.
Finally, we believe that major progress has been made in the past several
months and that it is now possible to do the Veterans Administration
Epidemiology Study, looking not only at Vietnam exposure but exposure to
Agent Orange. We view as the only remaining factors that will prevent the
successful completion of this study to be the degree of participation among
the selected veterans and the nonavailability of necessary resources.

Vernon N. Houk, M.D.
Chair, Science Panel
Agent Orange Working Group
3/5/82

�AGENT ORANGE WORKING GROUP
SCIENCE PANEL REVIEW OF PROPOSED PROTOCOL DESIGN
FOR VETERANS ADMINISTRATION EPIDEMIOLOGY STUDY

By School of Public Health
University of California at Los Angeles
The following represents a consensus of the reviewers of the proposed
protocol design. All reviewers were present except one and his detailed
comments were made available to the other members. The individual comments
are enclosed (Tab B).
Overall Design
We agree that the historical cohort approach is the appropriate one. One
member suggested more consideration be given to a case control approach but
all other reviewers felt this is not possible because there is no clear cut
definition of a "case." We also agree with the approach to try to make it
as compatible as possible with other large studies such as the Ranch Hand
and the Australian Study.
COHORT
Selection
The panel unanimously agrees that the Department of Defense (DOD) should
select the cohorts in accordance with Dr. Bricker's cohort selection paper
(Tab A). This will provide, we believe, for elimination of as much misclassification as is possible from the existing or potentially reconstructable
records. We believe it is absolutely essential that the identification and
assignment of these individuals to the different cohorts not be available
to the participants or to the investigators until initial analysis of the
data is completed. The Science Panel will oversee this cohort selection
process. The study investigators must be aware of the method used to
select the cohorts but must not be aware of the individuals placed in each
group.
Criteria For Each Group
We recommend that groups be composed of high probability of exposed Vietnam
veterans, high probability of nonexposed Vietnam veterans, and a non-Southeast
Asia veterans group. Some felt that it would be desirable to include a
Vietnam veterans group exposed midway between the first and second groups
in order to make an assessment of dose response. The consensus is that
though this may be desirable, the inclusion of the fourth group is not
essential nor critical to the study.
Sample Size
We agree that 6,000 in each cohort group is a reasonable figure. As the
study progresses and as more information becomes available from other
studies, this issue may need to be reexamined. DOD anticipates being able
to provide 12,000 in each of the study groups for selection.

�Proposed Exclusions from the Cohort Group
We believe it is unreasonable to exclude officers and multi-tour Vietnam
veterans. These may be separately identified so that appropriate analysis
can take place but they should not be excluded from the study.
QUESTIONNAIRE
Questionnaire to Personal Health Providers of the Individual Veterans
Some of the selected veterans may have had multiple health care providers
since returning from Vietnam. The panel doubts that many private physicians
will fill out detailed questionnaires on their patients and thus wonder
about the usefulness of this part of the study. The needed information may
have to be obtained in other ways.
Individual Veteran Questionnaire
The questionnaire as it now exists is unacceptable. It is overly long and
uses highly technical terminology which many people including many physicians
will not understand. We recommend that careful thought be given to the
information that is needed to be gathered, who will administer and where
the questionnaire will be administered (telephone, home visits, etc.), and
that the questionnaire be redesigned to meet those criteria. The questionnaire should be limited to information that is critical to the study and
that will be used in the analysis of the results.
Other Instruments
The psychological and neuropsychological instruments, all of which were not
available for review, should be evaluated and should include only information
that will be used in the analysis of the results and presented in a way
that would not be offensive to the participants.
Physical Examination
Data collected from the physical examination should be limited to those
items that will be used in the analysis of the study. This does not mean
that the physcial examination should not be comprehensive as determined by
the examining physician for the particular individual, although items to be
used for analysis of results must be collected according to a standard
protocol.
Laboratory
The final decision for the inclusion of laboratory tests for this study
should be made after consultation with laboratory scientists to ensure that
the best tests for that particular purpose are being used. There are other
tests such as chest x-ray, spirometry, nerve conduction tests, etc., that
probably have limited usefulness because of the inability to standardize
and to intrepret between multiple examining centers.

�It is critical that the standardization of laboratory procedures proceed
with quality control and quality assurance for collection, transportation,
handling, and analysis and that this process be begun immediately in the
participating laboratories.
Other Areas of Concern
For all participants, the panel believes that information should be
collected only on those items that are critical to the study, can be
standardized, and are such to appropriately interpret between multiple
examining centers and laboratories. If the practising physician feels that
additional information is necessary for a particular patient to evaluate
the health status, it obviously should be done but should not be part of
the overall data collection and analysis for the purposes of this study.
It is not clear from the proposed protocol the duration of the overall
study or time estimates for each individual participant. These should be
determined. A possibility that should be considered in regard to future
duration is that after completion of the initial examination and analysis,
the cohorts names be matched against the National Center for Health Statistics
(NCHS) Annual Mortality Index. This would provide nearly all of the
necessary followup information and would be more efficient than a mail
survey or a hands-on followup of each individual.
It should be explicitly stated in the final design that when an abnormality
for an individual is found, how that abnormality will be followed, who will
follow and treat it, and what system will be set in place to ensure that
each individual will receive the necessary medical care.
After the initial analysis has been completed and depending upon the results,
additional well focused, smaller studies, such as specific case control
studies, may be necessary to further define the extent of possible uncovered
problems.
After the initial analysis has been completed, the method of cohort selection
should be made public. While still ensuring individual confidentiality,
each participating veteran should be informed of his or her status in the
cohort selection process.
The panel assumes that the final protocol will address the usual concerns
of patient confidentiality, freedom to withdraw from the study, and methods
of providing the individual veteran specific medical information of which
he or she or his or her physician should be aware for the proper care of
the individual veteran.
Pilot Study
We believe the Pilot Study should include 5 percent of the anticipated
study population. We recognize it may not be possible that this be a
random sample of the population but that it be clearly stated and understood
what that 5 percent represents. The panel unanimously disagrees that the
Pilot Study should take place in only one study site but recommends strongly
that it be conducted in all examination centers and study sites that will

�be used in the overall study. The Pilot Study should be used to determine
participation rates and to further refine the instruments to be used in
this study. An analysis of the results of the pilot study can be used to
make a determination of the possibility of success of the larger study.
The results should in no way be interpreted as to effects but only whether
it is possible to conduct a scientifically valid overall study.
Summary
On the basis of the present document, the panel believes it is possible to
begin the pilot phase of the study. The selection of the cohort for the
Pilot Study should immediately proceed as well as the quality control and
quality assurance procedures, the redesign of the questionnaire, and the
determination of comparability and interpretation of some of the proposed
instruments, such as nerve conduction studies, spirometry, etc., between
examining centers. Finally, we believe that major progress has been made
in the past several months and that it is now possible to do the Veterans
Administration Epidemiology Study, looking not only at Vietnam exposure but
exposure to Agent Orange. We view as the only remaining factors that will
prevent the successful completion of this study to be the degree of
participation among the selected veterans and the nonavailability of
necessary resources.

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Houk, Vernon N.

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Report/Article Tltlfl Memorandum from Chair, Science Panel, Agent
Orange Working Group, to Members, Science Panel,
Agent Orange Working Group, Subject: Minutes of
January 27 Meeting, dated February 2, 1982

Journal/Book Title
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1982

Month/Day
Color
Number of Images

D

3

Tuesday, March 19, 2002

Page 5584 of 5611

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Public Health Service
Centers for Disease Control

Memorandum
Date
From

February 2, 1982
Chair, Science Panel

Agent Orange Working Group
Subject Science Panel Meeting Minutes
To

Members, Science Panel
Attached are the minutes of the last Science Panel meeting. Please return
your comments to me by February 16 so that I may finalize the comments.

Vernon N. Houk, M.D.
Attachment

�MINUTES OF THE SCIENCE PANEL
AGENT ORANGE WORKING GROUP

The Science Panel met on January 27, 1982.
is appended. '

A list of the attendees (Tab A)
'

Status of Fat Biopsies

i
The Chairman of the Fat Biopsy Subcommittee reported that the Subcommittee is
developing a report to the Science Panel on fat biopsies for dioxins that will
include information on (a) what is currently known and the current status,
(b) when we would recommend it be done and under what circumstances, and
(c) its limitations. It is anticipated that this report will be available
within 6 weeks.
Protocol Review
The Science Panel completed its review of the National Cancer Institute (NCI)
"A Case-Control Study of Lymphoma and Soft-Tissue Sarcoma: Association with
Herbicide Exposures." It was agreed that the individual reviews will be
returned to NCI. In general, the Science Panel was supportive of the
proposal, and several agencies offered to help provide specific information.
We further noted that this study should be complementary to the NIOSH proposed
case control study on soft tissue sarcoma. The two studies are not exclusive
of one another.
Veterans Administration Mortality Study
The Chairman of the Subcommittee reviewing the VA Mortality Study reported to
the Science Panel. There was "considerable discussion about the proposed
study's ability to answer the question. Most but not all members feel that a
proportional mortality study of all of the death certificates may be desired.
Though the BIRLS tapes data are generally considered to be accurate and
complete, there is question about the accuracy and completeness of the proposed
Department of Defense (DOD) tapes that are going to be used for matching data.
The Science Panel requested the subcommittee continue its work and report
within 6 weeks on various options and resource requirements for each option to
address this issue. The VA provided information (Tab B) on the numbers of
individuals involved for the proposal as it was submitted.
Agent Orange Troop Exposure and Non-Exposure Cohort Selection Concept Paper
The DOD'provided further details (Tab C). It is agreed that it is possible to
develop cohorts of exposed and nonexposed units. It is anticipated that the
Science Panel will recommend to the Agent Orange Working Group that a letter
detailing the proposal and requesting that it be completed be sent from Secretary
Schweiker to Secretary Weinberger.
In addition, a review of the disposal of herbicide waste and a trip report by
the DOD assessing the herbicide usage in Vietnam were made available to the
Science Panel (Tab D).

�Assessment of Agent Orange Health Hazards Among the Vietnam Population
Recent press reports of a group returning from Vietnam indicated that the
Government of Vietnam would welcome assessment of the health risks in the
Vietnam population by American scientists. There is concern about the status
:
of the records and the availability of those records in Vietnam.
Dr. T. E. Woodward, VA distinguished physician, reported that he found the
records to be useful. There was general agreement that a study would be
difficult to do and difficult to interpret. The members of the Science Panel
were asked to provide written comments to the Chair within 2 weeks. A concensus document will then be developed for transmission to the Agent Orange
Working Group.
Health Problems of U.S. Military Veterans and Possible Exposure to Phenoxy
Acid Herbicides in Vietnam: Partial Coding and Statistical Analysis of the
Citizen Soldier Health Questionnaire (CSHQ)
Dr. John Moore made available to the Science Panel the final report to the
National Toxicology Program of the statistical analysis by Dr. James H. Dwyer
and Mr. Robert Smith of the New York State University at Stony Brook (Tab E).
Public Information
A member of the Science Panel expressed concern that the public does not have
information available to counter some of the claims of adverse health effects
which are not yet proven. There was general discussion of this topic. Most
members feel that there is insufficient data to make firm statements on these
issues at the moment. It was* noted that the Scientific Panel under the
direction of Dr. John Moore prepared such a document that was released at the
public meeting of the Agent Orange Working Group held in September 1980. A
copy of that document will be reviewed to determine if any additional information is available. The members of the Science Panel were asked to communicate
their thoughts in writing to the Chair, and this will be discussed further.

Vernon N. Houk, M.D.
Chair, Science Panel
Agent Orange Working Group

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Orange Working Group, to Members, Science Panel,
Agent Orange Working Group, Subject: Minutes of
December 14 Meeting and Draft Memorandum to Chair,
AOWG, dated December 17, 1981

Journal/Book Title
Year

1981

Month/Day
Color

Number of Images

D

°

Descrlptoo Notes

Tuesday, March 19, 2002

Page 5581 of 5611

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Date

Public Health Service
Centers for Disease Control

.December 17, 1981

(404) 452-4111
FTS 236-4111

From

Chair, Science Panel
Agent Orange Working Group

Subject

Minutes of December 14 Meeting and Draft Memorandum to Chair, AOWG

To

Members, Science Panel
Agent Orange Working Group
Attached are the minutes, of the last meeting and a memorandum to the Chair,
Agent Orange Working Group concerning the Wisconsin Mapping proposal.
Please provide your feedback by January 14.
The next meeting will be January 14, 1982, 9 a.m., in Room 729G of the Hubert
Humphrey Building, Washington, DC.

ernon N. Houk, M.D.
2 Attachments

�DRAFT

MINUTES OF THE SCIENCE PANEL
AGENT ORANGE WORKING GROUP

The Science Panel met on December 14.
appended.

A list of the attendees (Tab A) is

The Science Panel notes with pleasure that Dr. Peter Greenwald, Director,
Division of Resource Centers and Community Activities, National Cancer
Institute, has been invited to membership on the Science Panel.
Documents Distributed.to the Members;
Texas State Veterans Agent Orange Act, H. B. No. 2129 (Tab B).
Associated Press release on the State of Wisconsin veterans populations with
alleged health effects of Agent Orange (Tab C).
Jennifer A, Hanify, et al, "Aerial Spraying of 2,4,5-T and Human Birth
Malformations: An Epidemiological Investigation," Science, Vol. 212, 17 April
1981 (Tab D).
Kingsley M. Stevens, "Agent Orange Toxicity:
Human Toxicology (1981), Vol. 1 (Tab E).

A Quantitative Perspective,"

"The Public Health Conference on Records and Statistics, The People's Health:
Facts, Figures, and the Future," DHEW Publication No. (PHS) 79-1214 (Tab F).
Protocols Received
Dr. Shelia K. Hoar, Environmental Epidemiology Branch, National Cancer
Institute, submitted a research protocol, "A Case-Control Study of Lymphoma
and Soft-Tissue Sarcoma: Association with Herbicide Exposures," to the
Science Panel for review (Tab G). The Chair asked for individual comments by
January 15, 1982. These comments will be consolidated and returned to
Dr. Hoar.
Agent Orange Troop Exposure and Non-Exposure Cohort Selection Concept Paper
The Department of Defense transmitted on December 4, 1981, a proposed Agent
Orange troop exposure and nonexposure cohort selection concept paper (Tab H).
From this concept, DOD indicated that it would be possible to identify groups
of personnel down to the platoon level who have had certain characteristics
of exposure to Agent Orange. These would include being within a kilometer
within 7 days of fixed wing herbicide spraying, stationed in base camps with
perimeter spraying, being associated with the so-called "aborted missions,"
etc. Other groups could be identified who would not have any of the above
characteristics. An additional group could be identified from serving in the
same time frame in southern continental United States bases where no herbicides were used.
These groups could then be the basis of the VA Morbidity
Study. The DOD was aksed to provide and report more specific details in the
next meeting on January 14, 1982,

�Wisconsin Proposal for HERBS Tapes Data for Mapping
At a previous meeting the proposal from Wisconsin to the Veterans Administration
to develop detailed, accurate, and reliable map series or atlas based on the
HERBS tape data depicting the dates and locations of herbicide spraying
missions conducted in the Republic of South Vietnam had been distributed
and comments requested. In general, it was felt that to be useful, the maps
should be accurate and reliable. Because they would not include information
on base perimeter spraying and the so called "aborted missions," it was felt
they would not be scientifically useful since they would be incomplete. Using
the data on the HERBS tapes alone would require mapping on a 1:50,000 scale
and would require approximately 1500 maps. The Chair will develop recommendations to the Agent Orange Working Group that contains the consensus of the
entire Science Panel to be delivered to the Agent Orange Working Group at its
next meeting in January.
Veterans Administration MortalityJ5tudy_
The preliminary protocol for the Vietnam veterans study was again discussed.
Serious concerns were raised the accuracy of the DOD computerized records that
are being proposed for this study. The Science Panel members had divergent
views on whether the study should be of the total Vietnam veterans death
records or whether sample techniques could be used. A subcommittee was formed
to review this matter and make recommendations to the Science Panel at the
next meeting on January 14. The subcommittee to be chaired by Dr. Kimbrough
also includes Drs. Greenwald, Keller, Brown, and Shepard. Dr. Greenwald also
discussed the Upstate New York Mortality Study.

Vernon N. Houk, M.D.
Chair, Science Panel
Agent Orange Working Group

�DRAFT 12/17/81

FROM:

Chair, Science Panel
Agent Orange Working Group

SUBJECT:

TO:

Wisconsin Proposal for HERBS Tapes Data for Mapping

Mr. James Stockdale
Chair, Agent Orange Working Group

At a previous meeting the proposal from Wisconsin to the Veterans
Administration to develop a detailed, accurate, and reliable map series or
atlas based on the HERBS tape data depicting the dates and locations of
herbicide spraying missions conducted in the Republic of South Vietnam had
been distributed and comments requested (Tab A).

The following is a consensus recommendation to you from the Science Panel.
If you concur, we recommend it be forwarded to the Veterans Administration.

While the Science Panel agrees in principle that detailed maps could be
made available to others for the purpose of determining exposure to Agent
Orange in Vietnam, we have serious reservation because it is unlikely that
they would be sufficiently accurate to determine proximity to exposure in
all instances.

A mapping of only the HERBS tapes locations would require from 1,200 to
2,000 maps on a minimum scale of 1:50,000.

There are sufficient errors on

the HERBS tapes that would not allow exact locations of all fixed wing
spraying missions.

In addition, very few of probably hundreds of

helicopter spraying missions around fire bases, along roads, lines of
communications, and along rivers are documented in the HERBS tapes.

�Similarly, perimeter spraying from trucks and by backpack sprayers could
not be adequately documented.

While we agree in principle that we should

make everything available, it is our consensus that if. the maps are
inaccurate and so voluminous as not to be useable that they in fact will do
a disservice.

One can argue that detailing the limitations of the maps is

an approach to being able to provide them.

It is our experience that those

caveats are not always recognized and the maps are used as "gospel" without
full understanding of their limitations.

This would also be costly and

would not successfully compete for the scarce resource dollars available
for health studies.

Thus, there are public relations reasons for approving this proposal but
scientific reasons for not doing so.
and usefulness.

Those scientific reasons are accuracy

The Science Panel would recommend at this time that the

Veterans Administration be advised not: to financially support such a project.

Vernon N. Houk, M.D.

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"m

Author

Houk, Vernon N.

CorDOratB Author

Department of Health and Human Services

RepOrt/ArtiClB TItiB

The

D

Perception of Risk

Journal/Book Title
Year

1984

Month/Day

October 15

Color

D

Number of Images

15

DBSCriptOn NOtBS

National Conference on Environmental Public Health,
Ramada Inn Central, Atlanta, Georgia

Wednesday, January 16, 2002

Page 4174 of 4258

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Public Health Service

Centers for Disease Control
Atlanta GA 30333

FOR RELEASE ONLY UPON DELIVERY

THE PERCEPTION OF RISK

Vecnon N. Houk. M.D.

Director
Center for Environmental Health
Centers for Disease Control
and

Assistant Administrator
Agency for Toxic Substances and Disease Registry
Public Health Service
Department of Health and Human Services
Atlanta, Georgia 30333

National Conference on Environmental Public Health
Ramada Inn Central
Atlanta, Georgia

October 15, 1984

�INTRODUCTION

Risk may be defined in various ways.

Risk can be considered

the possibility of loss, injury, disadvantage, destruction,
contingency, or danger.
equivalent to threat.

Risk can also be considered to be
A risk can be considered to be someone

or something that creates or suggests a hazard or an adverse
chance, a dangerous element or factor.

In recent years, risk assessments and risk analyses have become
increasingly sophisticated.

This is an extremely difficult

area which is not based on objective science but primarily on
judgment and our concepts of risk.

The most important issue is how we perceive risks and what we,
as a society, feel are acceptable.

The United States has

emerged from an era where the main concern of society was
survival to an era where our main preoccupation seems to rest
on extending longevity and improving the quality of life.

This

philosophy is in conflict with our increasing suicide rate
among young people; our continued abuse of recreational drugs,
alcohol consumption, and cigarette smoking; and our motor
vehicle injury and death rates.

�What are the risks or hazards that we are concerned about, and
how do we perceive them?

In order to analyze differences in

our perception of risk, it first needs to be determined what
the risks are that we encounter in our daily lives, what the
frequency of injury from such risk is. and finally, how we
consider and deal with these risks.

These various risks are

listed in tables which I will now show (Numbers 1 - 5 ) .

ESTIMATED FATALITIES PER YEAR IN THE UNITED STATES
(TAKEN FROM 1979 VITAL STATISTICS)

1.

TOTAL DEATH/YEAR

1.914.000

2.

MAJOR CARDIOVASCULAR DISEASES

958.000

3.

MALIGNANT NEOPLASMS

403.000

4.

HOMICIDE

52.000

5.

SUICIDE

27.000

6.

MOTOR VEHICLE FATALITIES

50.000

7.

OTHER CAUSES

824.000

�—#2

WHAT ARE THE CHANCES (BASED ON DEATH RATES)?

1.

A 1 OUT OF 2 CHANCE OF DYING FROM A MAJOR CARDIOVASCULAR
DISEASE.

2.

A 1 OUT OF 4 OR 5 CHANCE OF DYING FROM CANCER.

3.

A 1 OUT OF 40 CHANCE OF GETTING MURDERED.

4.

A 1 OUT OF 40 CHANCE OF GETTING KILLED IN AN AUTOMOBILE
CRASH.

5.

A 1 OUT OF 70 CHANCE OF COMMITTING SUICIDE.

—#3

WHAT ARE THE CHANCES PER YEAR FOR THE U.S. POPULATION (220
MILLION)?

0.9% (9/1.000) OF THE POPULATION DIE OF ALL CAUSES.
0.44% (4/1.000) DIE OF MAJOR CARDIOVASCULAR DISEASES.
0.18% (2/1.000) DIE OF CANCER.
0.02% (2.4/10.000) DIE OF HOMICIDE.
0.012% (1.2/10.000) DIE AS THE RESULT OF SUICIDE.
0.02% (2.2/10.000) DIE AS THE RESULT OF MOTOR VEHICLE CRASHES.

�—#4
MOTOR VEHICLES - HAZARDS AND PREVENTIVE MEASURES

*

ONE INJURY IN 50 - 60 PEOPLE PER YEAR.

*

50.000 FATALITIES PER YEAR.

*

ONLY 11% OF CAR OCCUPANTS WEAR SEAT BELTS.

*

IF 75% OF THE POPULATION WORE SEAT BELTS.
14,000 LIVES PER YEAR COULD BE SAVED.

*

AIRBAGS WOULD RESULT IN A 50% REDUCTION
IN FATALITIES, SAVING 25.000 LIVES PER YEAR.

--#5
FACTS ABOUT CIGARETTE SMOKING

1.

THE SMOKE FROM rr^r CIGARETTE/DAY IS A VIRTUALLY SAFE DOSE
£* \J \J

FOR THE NONSMOKER.
2.

TOBACCO'S CONTRIBUTION TO CANCER DEATHS IS ESTIMATED TO BE

30%.
3.

CIGARETTE SMOKERS HAVE TOTAL CANCER DEATH RATES TWICE THAT
OF NONSMOKERS.

4.

HEAVY SMOKERS (MORE THAN 1 PACK A DAY) HAVE A 3-4 TIMES
GREATER EXCESS RISK OF CANCER MORTALITY.

5.

85% OF LUNG CANCER CASES ARE DUE TO CIGARETTE SMOKING.

6.

LUNG CANCER DEATHS IN THE UNITED STATES INCREASED FROM
18,313 IN 1950 TO 90,828 IN 1977.

�Faced with these statistics and with a limited amount of
resources, we should examine whether it is necessary to reduce
the risk from exposure to suspect carcinogens as it is now
suggested by some to a theoretical incidence of one excess
cancer in a population of 1,000.000 or one in 100,000.

Before we examine that question, I would briefly like to show a
slide giving some examples of human carcinogens.

(Slide #6)

EXAMPLES OF HUMAN CARCINOGENS AND LIFESTYLE FACTORS INFLUENCING
THE INCIDENCE OF CANCER
(66 - 88% OF CANCERS ARE ENVIRONMENTALLY INDUCED)

AFLATOXIN

HEMATITE

VINYL CHLORIDE

4-AMINOBIPHENYL

MUSTARD GAS

SOOT AND TARS

ARSENIC

2-NAPHTHYLAMINE

IONIZING RADIATION

ASBESTOS

NICKEL

ULTRAVIOLET LIGHT

BENZENE

STILBESTROL

TOBACCO

CADMIUM OXIDE

ALCOHOL

DIET

CHROMIUM

INFECTION

As this slide shows, it has been estimated that 66 to
88 percent of all cancers are environmentally induced. To
this. I would like to add that there is, to some extent, a

�genetic predisposition to the development of cancer.

In

talking about environmentally induced cancers, this does not
mean that these cancers are necessarily induced by synthetic
chemicals, that is chemicals made by industry.

Lifestyle

influences the incidence of cancer more than the exposure to
industrial chemicals in "low" concentrations.

In addition,

smoking is a major cause of cancer, and we should not forget
infectious diseases as has recently been demonstrated again
very dramatically with the association between Acquired
Immunodeficiency Syndrome (AIDS) and Kaposi sarcoma.

That lifestyles affect the incidence of cancer is vividly
demonstrated by the changing incidence of specific types of
cancer in migrating populations. For instance, the incidence of
cancer of the stomach in Japanese living in Japan is much
higher than in Japanese and their descendants who have
immigrated to the United States.

In contrast, cancer of the

breast in females in Japan is much lower than in Japanese
females who have immigrated to Hawaii or to the United States
and in their descendants.

Both Japan and the United States are

highly industrialized countries so that exposure to industrial
chemicals in these two populations would most likely be
similar; however, the lifestyles and eating habits of these two
groups are different.

Having examined these facts, let us now look at how risk
assessments have been conducted in the last few years in the

�United States and what impact they may or may not have on
preventing disease.

There are a number of industrial chemicals

now which have been shown to cause cancer in rodents when
rodents are exposed to these chemicals at high doses through
gastric lavage. inhalation, or direct skin application.

The

doses at which these chemicals cause cancer in small groups of
rodents varies.

This may somehow be related to their degree of

toxicity although such relationships have not been examined in
detail.

Some believe that any amount of a carcinogen, be it

ever so small, is capable of inducing cancer in the host if the
host receives any dose of such a chemical.

Others do not

believe this.

For example, a very basic concept in toxicology is that for
each chemical, there is a dose-response relationship.

This was

first pointed out by Paracelsus, who stated it in a negative
way, "Dosis sola facit, vt venenum non fit," which in English
means "The doses alone makes a thing not poison."

In other

words, reducing the amount given will render the chemical
harmless.

Commonly, the aphorism is seen as "Dosis sola facit

venenum" (Dose alone determines poisoning).

In most instances, animal studies have used high dosage levels
of the chemical to be tested, and the results of such studies
have then been extrapolated to lower untested dosage levels in
the animals.

With such extrapolations estimates have been made

�to determine at which point only one excess cancer in a
population of a million or one cancer in population of 100.000
would occur.

For these extrapolations, most recently,

multistage models have been used, and it has been assumed that
the dose-response curve would be more or less linear for all
carcinogens.

Very few studies have examined the dose-response relationship
of carcinogenesis more extensively.
conducted with rather high doses.

Most studies have been
In the United States only

one study (Staffa and Mehlman, 1979) was conducted in mice
where large numbers of animals (24,000 mice) and several dosage
levels of N-2-Fluorenylacetamide 2-FAA (30, 35, 45. 60, 75,
100, and 150 ppm) were employed.

The results of this study

suggest that perhaps the linear quantal non threshold model is
inconsistent with the data.

This leaves many questions about

"risk assessments" as they are usually modeled.

Most likely, at very low dosage levels, antioxidants. such as
vitamin E, vitamin C. selenium, and unsaturated fatty acids,
would have a protective effect against naturally occurring and
man-made carcinogens which cause lipid peroxidation.

The

contribution to cancer that very low doses of carcinogens would
make might well be overriden by lifestyle in general and would
be modified by dietary intake of natural antoxidants and thus
may not greatly contribute to the risk of cancer or other

�chronic diseases.

In other instances where the proximate

carcinogen is a metabolite, insufficient amount of such a
carcinogen may be produced at low dosage levels because of
alternate metabolic pathways. Furthermore, repair mechanisms
within the cell may have a protective effect against
carcinogens at very low dosage levels.

For most of the chemicals which have been shown to cause cancer
in animals, it is not known whether they actually cause cancer
in humans and if they caused cancer at what dosage levels they
would do so above background levels.

Since this information is

not available, extrapolations have been made from rodent
populations to human populations.

It is not at all clear at

this point, whether that is justified.

It can be stated that

all of the carcinogens that have caused cancer in humans also
cause cancer in animals.

The reverse is not true.

As more

carcinogens are identified, it has also become evident that
species variations exist.

For some chemicals it has been shown

that cancer can be produced in mice but not in rats, or cancer
can be produced in mice and rats but not in hamsters and
subhuman primates.

This depends to some extent on differences

in metabolism in different species.

Many of the parent

chemicals are indirect carcinogens and have to be modified in
the body to the proximate carcinogen.
chemicals may employ several pathways.

The metabolism of
It is possible, for

instance, that at low dosage levels, only one of those pathways

�is used, and at high dosage levels, this one pathway is
saturated and other pathways come into play.

In such

situations, the proximate carcinogen may only be formed at high
dosage levels.

This has never been extensively examined.

Furthermore, many chemicals that are classified as carcinogens
act as promoters of carcinogenesis.

It is not at all clear

what their effect would be at very low dosage levels.

Thus,

from rather insufficient animal data, extrapolationsd are made
to establish acceptable levels of risk for human populations.
The methods used appear to err on the conservative side, are
unsubstantiated by scientific data, and may grossly
overestimate risk.

In addition to all the uncertainties inherent in such risk
assessments, there are also many uncertainties about exposure
of populations to chemicals that are in the environment.

It

has not at all been determined with certainty, whether people
receive a dose at all from chemicals that are in soil and what
that dose is. We have made some estimates; however, we are
still in the process of conducting experiments to determine
whether such estimates are justified.

Thus, the scientific

data base is really not there to make these types of risk
assessments and to spend billions of dollars to reduce
exposures to such low levels that there would only be a
theoretical chance of getting one additional cancer in a
million population lifetime exposure.
10

�What needs to be done is to develop the scientific data base so
that more meaningful hazard evaluations can be made if humans
are exposed to chemicals which are suspect carcinogens.

Such

hazard evaluations should only be made in the context of
preventing disease in the future.

They should not be used to

establish a "cause-effect" relationship between nonspecific
cancer in a given individual and past exposure to low doses of
a suspect carcinogen.

In individual cases, such cause-effect

relationships cannot be established from animal data or from
epidemiological studies because of competing factors that come
into play at very low dosage levels.

The afore does not mean that we should not use "risk
assessment" in making decisions; however, we should recognize
that the process and the results are not as precise as some
would lead us to believe.

In doing risk assessments, we

emphasize carcinogenesis because of our concern that only a
small number of molecules may still cause cancer, while other
toxic effects would only occur at higher doses of the
chemical.

However, such risk assessments are only one part of

our armamentarium to estimate potential hazards resulting from
exposure to synthesized or naturally occurring chemicals.

For

example, foodstuffs such as peanut butter and cornmeal may
contain aflatoxin at concentrations which according to risk
assessment calculations would suggest that we should have an
epidemic of liver cancer in the United States, particularly in

11

�the Southeast, where these foods are consumed in large
amounts.

In reality, human liver cancer in the United states

is a rare event and is not increased in the Southeast.
Similarly, risks estimated for ethylene dibromide (EDB)
according to one calculation would suggest that if water
containing 1 ppb (mg/k) of EDB were consumed, this would result
in one additional cancer in each population of 1,500.

The

number of cancers would be even higher if humans were exposed
to higher concentrations.

It is curious that no data at all

suggesting a higher incidence of cancer in populations
occupationally exposed exists.

Until we do have greater precision using the risk assessment
instrument, I would suggest the following approach as
reasonable.

This approach would divide the process into

several factors.

1.

Substance hazard evaluation.

Is the substance known to be

hazardous to animals and humans if human data exist?
are the data?

What is the mechanism of action and how have

the dose response curves been calculated?

2.

If the substance is hazardous in animals, what is the
theoretical hazard to humans?
exposure?

What

Through what avenues of

Or through what mechanism of action?

12

�3.

Populations. Are there populations exposed to this
material, are the theoretical avenues of exposure possible,
and what is the likely degree of exposure?

4. Pilot studies.

Is there evidence in the population exposed

for continuous exposure?

Can such exposure be quantified

if the chemical is persistent in humans or can historical
data be used to assess this?

Based upon the action of the

chemicals in those most likely most highly exposed, are
there any biologic tests which could be used as an
indicator of exposure, or which could be used as an early
indicator of adverse health effects?

5. Health studies in the general population.

From analysis of

appropriately done epidemiologic studies, is there evidence
of harm to humans?

The public health role is one of prevention.

Even in the

absence of conclusive evidence that harm to humans has
occurred, if the data and evidence from laboratory animal
studies is sufficiently strong that harm may occur, then
preventing exposure to future populations is a reasonable
action.

Here the policymaker must address what the potential

harm is, what is the potential remedial action, what is the
cost of that remedial action, and is it warranted?

In

determining whether or not it is warranted, it should be borne

13

�in mind there are resource needs for other areas of known
beneficial intervention, such as providing prenatal care to
mothers-to-be, vaccination of children, improving the nutrition
of the general population, and trying to reduce the incidence
of homicide, automobile injuries and deaths, and improving our
quality of life, which might reduce the suicide rate and the
increased use of substances of abuse.

REFERENCE:

Staffa, J.A. and Mehlman, M.A. 1979. Inovations in cancer
risk assessment (EDi study). Pathotox Publishers, Inc., Park
Forest. South Illinois.

14

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10

American Insurance Association, National Conference on
Environmental Injury Compensation, L'Enfant Plaza Hotel,
Washington, D.C.

Wednesday, January 16, 2002

Page 4164 of 4258

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Public Health Service

Centers for Disease Control
Atlanta GA 30333

FOR RELEASE ONLY UPON DELIVERY

THE NATURE AND EXTENT OF SCIENTIFIC KNOWLEDGE

Vernon N. Houk, M.D.
Director
Center for Environmental Health
Centers for Disease Control
and
Assistant Administrator
Agency for Toxic Substances and Disease Registry
Public Health Service

Department of Health and Human Services
Atlanta, Georgia 30333

American Insurance Association
'National Conference on Environmental Injury Compensation
L1Enfant Plaza Hotel
Washington, D.C.

March 19, 1984

�There are four myths that abound in this country of ours concerning the
potential health problems associated with low dose chronic human exposure to
toxic substances in our environment.

The myths are that:

These problems can be solved by hands on physical examinations of
individuals.

These problems can be solved by establishing registries of all
individuals exposed to hazardous

substances.

These problems can be solved by the collection of information on the
occurrence of diseases in all individuals and the analysis of this
voluminous set of data.

The scientific process available for studies in humans can give
conclusive cause and effect information for an individual's state of
health.

However, the fact that I recognize these as myths does not mean that I think
we cannot reasonably estimate risks from exposure among population groups.

Over the past decade, scientists have expended many millions of public and
private research dollars in efforts to investigate and understand the complex
relationships between human health and exposure to suspected environmental
pollutants.

The basic tools for this ongoing search are laboratory studies in

�animals and epidemiologic studies on humans.

Properly done, animal

experiments and epidemiologic studies provide a basis for identifying
associations between various human health risks and environmental factors,
from which public health and environmental protection policies are developed
to minimize the risks to current and future populations.

Information obtained

from the use of these tools—animal toxicology studies, and human
epidemiologic investigations—have been misapplied in many instances to
diseases in individuals because of a failure of the scientific community to
make clear the nature and the limitations of our knowledge about
environmentally related health risks.

We know there is an imminent threat

that this knowledge will be misunderstood and misapplied by those who do not
understand the process and want to use it for other purposes; we should be
careful to prevent that from happening.

A number of diseases exist which are known to be caused by exposure to certain
chemical or physical agents.
cause.

For some diseases, there is no other known

Such diseases include asbestosis, radiation sickness, Caisson's

disease (decompression illness), and mesothelioma, which is usually caused by
asbestos.

Most documented frank illnesses caused by chemicals are encountered

as (1) occupational ^iseases; (2) effects of mishandling or overexposure to
pesticides including germicides; and (3) acute and chronic poisoning episodes
(e.g., those involving arsenic, mercury, and lead).

In the case of some other illnesses, the chemical-disease link is strong, but
not unique.

Vinyl chloride causes a rare cancer of the liver, the

�Two areas present us with some of the most complex and perplexing scientific
problems faced by public health officials today.

These are related to the

establishment and maintenance of registries of exposed persons and to
determining the relationships between exposure to toxic suostances and
illnesses.

We are attempting to answer the question:

What are the increased

risks of long-term health effects to persons exposed to hazardous substances?
One of the most commonly recommended tools for studying the chronic or
long-term effects of exposure is to construct a registry of persons exposed.
The persons in the registry can be tested periodically to determine their
health status and eventually to determine the cause of their death.

Registries cannot be used to give quick conclusive answers to the many
questions that people ask about the effects of toxic chemical exposure on
their health, the health of their families, or the health of their future
children.

Even the most active and aggressively pursued studies using

registries may require decades to produce meaningful results,

it is also true

that even when the results of long-term studies are made available, the
findings are likely to be hotly debated by scientists who honestly represent
different points of view.

Other important limitations of registries are

infeasibility due to mobility aad privacy and inability to detect conditions
with a low attack rate after exposure; even cost must be considered.

I point

out these inherent limitations in registries to call to your attention the
fact that expectations for registries being used as tools to answer in the
near future the questions before us today may be unrealistically high.

�Some questions are:

What measures of exposures should be used to set guidelines for
eligibility for inclusion in a registry?

To what extent are people willing to participate over the course of a
lifetime in active followup registries—a constant, stressful
reminder of the fact that they were exposed to a toxic substance?

How can we assure that a commitment made today to establish and
maintain a registry will be carried through over a period of 10, 20,
30, or 40 years?

What level of followup is necessary, scientifically, to provide
estimates of risk which can then be used to make sound decisions to
manage the risk?

Even with these limitations, the Public Health Service has a commitment to the
use of registries, where appropriate, to attempt to clarify the link between
toxic exposures and adverse health outcomes.

We now have a group trying to

determine where they are appropriate.

We are likewise committed to use the other tools at our disposal
—epidemiologic and other—to demonstrate the links where they exist.

Many of

the epidemiologic tools, unless impeccably used with large enough populations

�will yield inconclusive results—neither positive or negative.

Unfortunately

some people will use inconclusive- results that tend toward the negative as
definitely negative results; others claim inconclusive results which tend
toward the positive as unequivocally positive results.

Both are incorrect.

Inconclusive results are simply that, inconclusive!

What becomes evident is that many factors influence the development of
disease.

Since some illnesses, including many cancers, may have latency

periods of 20 to 40 years; and since in general, environmental exposure to
man-made chemicals has been at relatively low concentrations through a variety
of routes—that is, inhalation, ingestion, absorption through the skin—it is
presently impossible to determine for the individual precisely what events led
to the development of disease.

The state of the art in medical science or

epidemiology is not such that we can predict with certainty whether a person
who has been exposed to chemicals will ultimately develop a particular disease
or condition.

In most cases then, the conclusion must be drawn that the

scientific data base presently available does not permit with certainty a
determination of whether exposure has a causal relation to illness occurring
in an individual or not.

Presently available data do provide sufficient

evidence to reduce exposure, and thus possibly prevent disease in the future.
There is a reason for this dichotomy between prevention and attribution of
cause.

The studies which generate information about the chronic low dose

toxic effects of chemicals do not permit predictions with full confidence
about the health of an individual, but rather only about the health of a
population and what the degree of risk a given population will run if it
continues to be exposed.

�Proper use of the scientific data can lead to important collective public
health benefits; use of the data for that purpose would be both responsible
and just.

On the other hand, to press such data into service to respond to

causal effects for an individual's disease holds high potential for misuse of
the data.

Epidemiologic studies almost never prove cause and effect, though in a few
instances reasonable people would accept them as such.

For example, in

looking at the pathway of exposure and body burden, the association of the
reduction of lead used in gasoline production and the reduction of mean blood
lead levels in the U.S. population.

Over a 4-year period when the lead

phasedown in gasoline was occurring, we were conducting a study of blood lead
levels in the U.S. population, the Second National Health and Nutrition
Examination Survey.

Two things, declining blood lead levels in children and

lead used in gasoline production, were associated with a correlation
coefficient of .95; this could have occurred by chance in less than one in
10,000 times.

We removed over 200 possible confounders from the association

and the coefficient did not appreciably change.

Yet many said this did not demonstrate cause and effect.

We agree!

The only

way in this situation to conclusively prove cause and effect would be to place
children in chambers breathing air contaminated with differing lead levels and
then measuring the blood lead levels in these children.
in a society where this kind of study is not possible 1
purposely expose individuals to hazardous substances.
must use only inadvertent exposure where that occurred.

Fortunately, we live
It is not ethical to

Studies done in humans

�We will continue to respond to specific incidents of human exposure to toxic
or hazardous substances.

We will also continue our efforts to measure both

the immediate and long-term health effects and to make sound recommendations
for the attenuation of the risks.

Although the results of our studies may not provide the conclusive answers
about health risk which are so much in demand, we have hope that we can
demonstrate strong associations, where they exist, between exposure and
adverse health outcomes so that reasonable people can take reasonable actions
to protect public health and the environment.
role as primarily one of prevention.

Thus, we see the public health

Causal attribution in an individual

must be done with great caution and except in rare circumstances cannot be
done with certainty when the exposure has indeed been of the low dose, chronic
form.

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01353
Houk, Vernon N.

Corporate Author
Report/ArtidO TltlO Memorandum: to Ronald W. Hart, Chairman, Science
Panel, Agent Orange Workinh Group (AOWG), from
Vernon N. Houk, Assistant Surgeon General, with
subject Protocol for Women's Vietnam Veterans Health
Study, September 10,1987

Journal/Book Title
Year

000

°

Month/Day
Color

D

Number of Images

4

DOSCrlptOn NOtBS

Memo discusses concerns that Houk has about the
study protocol. He wants the concerns addressed
before he will be willing to support conduct of the study.

Wednesday, July 11, 2001

Page 1854 of 1870

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Public Health Service
Centers for Disease Control

Memorandum
Date

.September 10, 1987

From

Director
Center for Environmental Health and Injury Control

Subject

Protocol for Women's Vietnam Veterans Health Study

To

Ronald W. Hart, Ph.D.,
Chairman, Science Panel
Agent Orange Working Group
We have reviewed the Women's Vietnam Veterans Health Study Protocol
submitted by the Hew England Research Institute, Inc. We have serious
concerns about this submission which we have listed below. Until these
concerns are adequately addressed, I cannot support conduct of the
proposed study. Detailed below are comments on the protocol for the
Women's Veteran Health Study.
A. Cohor^ Selection
1. Unlike the Vietnam Experience Study, there are differences
between the exposed group and the comparison groups in variables
other than experience in Vietnam. The presence of such
differences increases potential confounding and complicates the
analyses. Would it be more satisfactory to limit the scope of
the study and the selection of a comparison group (e.g., Limit,
the study to army cases and controls) to address the most
important hypotheses rather than try to do too much?
2. It is not clear how the VA developed its list of 5000 Army
Vietnam veterans—how complete is this list? How complete are
the lists of Vietnam veterans in the other services?
3. The sampling frame for the non-Vietnam veterans is not clearly
described.
4. How valid is their proposed capture-recapture method as a method
of documenting the completeness of the cohorts.
5. What duty stations will women veterans for Cohort B come from?
Will the Air Force sample of nurses be large enough for separate
comparisons?
6. pages 2-3: What does matched on occupation mean and how will this
be possible?
7. Consideration might be given to increasing the number of controls
(per case) in the overall study, especially in some of the
proposed substudies (e.g., reproductive health).

�Page 2 - Ronald W. Hart, Ph.D.
B. Reproductive Health
1. The expectation is to find major birth defects in 1% of
offspring; a more appropriate expectation is 2-3%. It would be
wise to compile a list of specific defects which are to be
considered "major" before the study begins.
2. Cases are defined as women who have had a baby with a defect or
"two or more spontaneous abortions not clearly attributable to an
identified cause." They propose excluding those with an
1
"unequivocal karyotypic abnormality", and those with a uterine
abnormality. Exclusion of women who themselves have a tcaryotypic
abnormality seems reasonable, but it is unlikely that any will be
found in the sample. If the reference implies that aborted
fetuses that have a karyotypic abnormality will be excluded, this
is not reasonable. An abortion associated with a chromosomal
anomaly is a health outcome worth considering in the study. In
general, more details are needed on why certain
diseases/conditions are being excluded.
3. Spontaneous abortions will be difficult to validate since they
are frequently not medically documented.
4. It is stated that women with diethylstilbesterol (DBS) exposure
would be kept in the sample. We would suggest exclusion since
they are excluding spontaneous abortions associated with uterine
abnormality, and DES exposed women have a higher rate of
abortion, usually from uterine abnormality.
5. We would suggest matching controls on age at the last abnormal
pregnancy, rather than the first. Spontaneous abortion is
strongly related to age and a woman's pregnancies may be
separated by many years.
6. At the time this study will be done, most women Vietnam veterans
will be 40 or more years of age. Therefore the evaluation of
prolonged amenorrhea should probably be deleted from the study.
7. A definition of fertility/infertility is needed.
C. PsycholoRical/KeuropsychoIoRical TestinR
1. The proposal to use the CDC Vietnam Experience Study (VES)
neuropsychological battery is inappropriate. That battery was
designed to assess primarily neuropsychological deficits which
might be expected from exposure to a toxin (e.g. TCDD). The
battery also included some assessment of psychological and
neuropsychological problems that might be related to stress.

�Page 3 - Ronald W. Hart, Ph.D.
This latter component is not included (as far as we can tell) in
the present protocol. Since TCDD exposure is unlikely to have
been a major problem for most nurses in Vietnam, it would
probably be better to give greater emphasis to long-term
psychological stress faced by these veterans while in Vietnam.
This would mean that the proposed battery should include some
measures of stress which have been well validated and accepted in
psychological research.
'

In addition, greater emphasis should be given to depression,
anxiety, and alcohol and drug use, which are possible sequelae of
stress. Also, consideration should be given to including the
Minnesota Multiphasic Personality Inventory (MMPI), and more of
the Diagnostic Interview Schedule (DIS) than just the Post
Traumatic Stress Disorder (PTSD) section.

2. Another concern in the psychological area is the testing in the
home of the participant. The VES battery was designed to be
administered in a standard testing environment by trained
technicians under close supervision. Quality control and
standardization will be difficult in the proposed setting.
3. The rationale for measurement of TCDD levels in the PTSD substudy
needs further clarification/justification.
4. With respect to the psychological area in general, we suggest
that advice be sought from experts in psychology/psychiatry to
evaluate the proposed psychological test battery. In addition,
staffing for the study should include a qualified psychologist or
psychiatrist.
D. Serum. Dioxin (TCDD) Measurement
1. The whole issue of Agent Orange exposure assessment/TCDD testing
becomes questionable now that the results of CDC's Validation
Study are known. If TCDD testing is to be done, is a whole unit
of blood necessary—if willing to accept some cut-off level (e.g.
20 ppt) less blood may be required. Also, if TCDD testing is to
be done, consideration should be given to using a sample of
Vietnam and non-Vietnam veterans—based on the results of a
sample, a decision could be made about testing other
participants.
2. Serum TCDD measurements are to be used as the measure of exposure
for both the Reproductive Outcomes Study and the Post Traumatic
Stress Disorder Study. Apparently about 550 serum analyses will
be needed for these two studies combined. The current proposal
does not involve flying the participants to a centralized
collection center but rather using local Red Cross Centers on
contract. These approximately 550 women will be located all over

�Page 4 - Ronald U. Hart, Ph.D.
the United States and the Red Cross is not even present in every
state, so obtaining the samples solely in this manner will not be
possible. A very large number (&gt;100) of Red Cross contracts will
be involved to obtain blood on persons near a Red Cross Center
under the current plan. The use of at least regional Red Cross
Centers would be a marked improvement and the quality of sample
acquisition would be significantly higher if only a few (even
one) Red Cross Center(s) were used.
3. T|he cost of the serum 2,3,7,8-TCDD measurement should be noted to
be $1000 apiece. Currently the protocol states that EHLS is the
only lab in the U.S. that can perform the measurements, but
clearance for such measurements at EHLS has not been obtained.
Similarly, has the American Red Cross been approached as to their
willingness to participate in this study?
E. Operational and Other Issues
1. The protocol anticipates a fair amount of dependence on both
interviews and military records. What are the limitations of
these data in terms of the questions addressed (e.g.,
ascertainment of spontaneous abortions by history)?.
2. The authors do not provide information on how they propose to
address the issue of name changes in female veterans and the
difficulties this might cause in locating these veterans.
3. The operational aspects of the pediatric examination component
are not clearly described. Has the Ranch Hand Study been
successful in this area? What end points will be looked at and
analyzed?
4. The choice of conditions to be validated might be expanded to
include same conditions which have been suggested to be
associated with TCDD exposure—e.g. skin conditions (chloracne,
hyperpigmentation, etc.), liver disorders including prophyria,
peripheral neuropathy, immunologic deficits.
5. Quality control of the physical and routine laboratory
examinations must be assured.
6. Has adequate effort been made to insure that the medical records
and pathology slides will be reviewed in a blinded manner?
7. What efforts are being made to insure quality assurance and
quality control of hormone blood testing?

Vernon H. Houk, M.D.
Assistant Surgeon General

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01734

Author

Houk, Vernon N.

Corporate Author
RepOrt/ArtiClB TltlO Memorandum: Review of VA Mortality Study, from
Vernon N. Houk to Ronald W. Hart, September 11, 1987

Journal/Book Title
Year

000

°

Month/Day
Color

D

Number of unaoos

2

Desorlpton Notes

Monday, June 11, 2001

Page 1785 of 1793

�DEPARTMENT OF HEALTH &amp; HUMAN SERVICES

Public Health Service
Centers for Disease Control

Memorandum
Date
From

.September 11, 1987
Director
Center for Environmental Health and Injury Control
Review of VA Mortality Study

Subject
To

Ronald W. Hart, Ph.D.
Director
National Center for Toxicological Research
i
The Veterans Administration (VA) has conducted a proportionate mortality
study (PMR) of 24,235 deaths among U.S. Army and U.S. Marine male
veterans who served in Vietnam and 26,685 deaths among male veterans of
the same two services who did not serve anywhere in Southeast Asia. All
deaths were identified from the VA BIRLS file and occurred between
July 4, 1965, and March 1, 1982. These deceased veterans had to have
served in the military sometime between July 4, 1965, and March 1, 1973.
Career and non-career, officers, and enlisted men, as well as reservists,
were included. In-service deaths occurring before 1974 and men dying
from war-related injuries were excluded. In service deaths after 1973
were included.
Within the group of Vietnam veterans, the fraction of all deaths
attributable to a particular cause was computed and compared to the
corresponding proportion for non-Vietnam veterans. The comparison was
done using the proportionate mortality ratio (PMR) technique in which age
at death, race, and branch of service were taken into account. There was
no adjustment for calendar year of death or rank. Altogether, PMRs were
computed for 18 major cause of death groupings and for 23 specific cancer
sites.
We will address our concerns in data collection, data analysis, and
interpretation.
Data Collection. Are the BIRLS tapes truly at least 94 percent
complete? From the CDC Mortality Study which used multiple sources of
mortality we found that BIRLS was less complete.
Data Analysis. Why do the authors emphasize only the statistically
significant positive findings? Why were not the significant decreases in
deaths from genitourinary diseases (Table 3) and the decrease in deaths
*. from all cancers for one-tour of duty veterans (Table 5) not discussed?
The lack of association between service in
be reevaluated in light of the CDC finding
in the first 5 years after discharge. CDC
discharge rather than year of death. This

Vietnam and suicide needs to
that they were increased only
used the time period since
subject was repeatedly brought

�Page 2 - Ronald W. Hart, Ph.D.
up with the VA prior to completion of their analysis. The CDC study
would indicate that grouping by 10 year periods would minimize the
effect.
The findings for lung cancer and NHL in Marine Vietnam veterans are
provocative, although similar observations were not made in other studies
of Vietnam veterans. The absence of unusual mortality from soft-tissue
cancers is consistent with some previous studies but at variance with
others. Because so many statistical tests were done on the data set,
these ^apparent findings could be due to chance. It would be helpful to
see a more detailed analysis in which mortality from these cancer sites
is examined by calendar year in Vietnam, rank, MOS, and principal duty.
These additional analyses would help in deciding whether some factor
related to the Vietnam experience is responsible for the apparent
association.
Interpretation. The authors suggest that these were major differences in
the findings of previous studies cited, but there are in fact few major
differences in the findings.
Referenced studies were not critically discussed. There has never been,
for example, an association demonstrated between lung cancer and phenoxy
herbicides except in the Zack Study (Ref. 29) where 3.6 cases were
expected and 6 were found in those exposed to 2,4,5-T. Those authors
state that they cannot evaluate trends in lung cancer deaths as they
relate to occupation because of "limitation in the data."
As noted above, it is not surprising to encounter the small number of
statistical departures from expected mortality seen in this study. These
could easily have arisen by chance alone. This study, as originally
designed, cannot conclusively clarify mortality risks for Vietnam
veterans, let alone elucidate possible causative factors within, or
outside of, the Vietnam experience. Reasons include lack of a defined
population-at-risk, incomplete ascertainment of deaths, and absence of
"exposure" data on individual veterans.
This PMR study appears to be well executed in mechanics. However, the
presentation and discussion of the results do not provide the necessary
caution in interpretation and allow the uninitiated to make causal
inferences where they do not exist.

Vernon N. Houk, M.D.
Assistant Surgeon General

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